Forest Nursery Notes Winter 2009 Using Polymer-coated Controlled-release Fertilizers in the Nursery and After Outplanting by Thomas D. Landis and R. Kasten Dumroese Controlled-release fertilizers (CRF) are the newest and most technically advanced way of supplying mineral nutrients to nursery crops. Compared to conventional fertilizers, their gradual pattern of nutrient release better meets plant needs, minimizes leaching, and therefore improves fertilizer use efficiency. In our review of the literature, we found many terms used interchangeably with controlled-release, such as slow-release, but in this article, we will simply refer to all of them as controlledrelease fertilizers (CRF). CRF can be divided into 3 categories based on their coating and nutrient composition: Figure 2 - Nutrient release patterns vary between fertilizer brands and formulations. For example, the nutrients in Osmocote® can be formulated in bands to release faster or slower during the growing season (modified from Hulme and Buchheit 2007). 1. Uncoated, nitrogen-based fertilizers – This oldest class of CRF consists of chemically-bound urea and the release rate is determined by particle size, available water, and microbial decomposition (Goertz 1993). Ureaform and IBDU are examples of uncoated, nitrogenbased fertilizers. With the exception of Agriform® tablets, which have been used at outplanting, this class of CRF is rarely used in forest, conservation, and native plant nurseries. 2. Coated, nitrogen-based fertilizers – Sulfur-coated urea was one of the first CRF and nitrogen release is controlled by the thickness of the sulfur coating (Goertz 1993). Although still used in agriculture, sulfur-coated urea is rarely used in forest, conservation, and native plant nurseries. 3. Polymer-coated multi-nutrient fertilizers – Polymer-coated CRF (PCRF) are the newest and most technically sophisticated fertilizers being used in horticultural plant production, and consist of a core of soluble nutrients surrounded by a polymer coating. Each polymer-coated fertilizer particle is known as a prill” (Figure 1A-B), and nutrient release is precisely controlled by the chemical composition and thickness of the polymer coating. Compared to the previous categories that only supply nitrogen, PCRF supply all 3 “fertilizer elements” (nitrogen [N], phosphorus [P], and potassium [K]), and many formulations include calcium, magnesium, sulfur, and micronutrients. The defining characteristic of PCRF, however, is the sophisticated polymer coatings that gradually release nutrients over extended periods; release rates can be as short as 3 months or as long as 18 months. Nutrient release from PCRF prills occurs by diffusion through a semi-permeable membrane. The process occurs in 2 stages (Gambash and others 1990). First, when Figure 1 - The individual particles of polymer-coated prills are exposed to moisture in the soil or growing mecontrolled release fertilizers (PCRF) are called “prills” dium, water vapor infiltrates into the prill and condenses and consist of soluble fertilizers inside a thin plastic on the soluble fertilizer salts, creating an increase in shell (A-B). After water penetrates the prills, soluble osmotic pressure. Second, this elevated pressure within nutrient ions move outwards into the soil or growing the prill causes the fertilizer ions to diffuse outward into medium along an osmotic gradient (C). (A and B the surrounding medium (Figure 1C) . courtesy of Scott-Sierra®.) 5 Forest Nursery Notes Winter 2009 active monomers over the fertilizer core in a continuous coating drum, resulting in an ultrathin polyurethane membrane coating. The result is a PCRF that delivers Several different brands of PCRF have been used in nutrients through a solute concentration gradient perforest and conservation nurseries in North America, and meation process that is unaffected by soil moisture, mithey can be categorized by nutrient content, release pat- crobial activity, or pH levels. A variety of Apex formutern, and longevity (Jacobs and others 2005). lations are available to meet the specific needs of conifers, woody plants, and native plants (Table 1). One Osmocote® (Scott-Sierra, Marysville, OH) is one of the formulation, Apex Native, is specially formulated for oldest PCRF and its coating is classified as a polymeric plants that are sensitive to high rates of P, and therefore aids in the colonization of mycorhizal fungi (Simplot resin. The coating is applied in several layers, and the 2008). relative thickness determines the speed and pattern of nutrient release at 70 oF (21 oC). Osmocote fertilizers are available with release periods from as short as 3 to 4 Multicote® and Nutricote® (Sun Gro Horticulture, months to as long as 14 to 16 months (Table 1). One Bellevue, WA) uses thermoplastic resin coatings recent innovation is called “patterned nutrient release”, blended with special release-controlling agents to deterwhich uses specialized formulations called bands to of- mine the nutrient release rate and longevity. Sun Gro fer specific release patterns (Figure 2). A wide variety markets 2 brands of PCRF—Multicote® in the U.S. and of Osmocote PCRF is available for different crops and Canada, and Nutricote®, which is only available in the production cycles including a “miniprill” formulation western U.S. (Sun Gro Horticulture 2008). Multicote® (Figure 1B) for small volume containers and miniplugs is available in a wide variety of nutrient formulations (Scotts Horticulture 2008). Although more expensive, with release rates from 4 to 16 months (Table 1). the smaller miniprills improved distribution between containers by 5-fold and reduced problems with uneven Diffusion® (Green Valley Agricultural, Caledonia, MI) growth (Drahn 2007). PCRF are customized for different temperature zones, and come in many nutrient formulations with longevities Apex® (J.R. Simplot, Boise, ID) uses the Polyon® Reac- from 3 to 9 months (Green Valley Agricultural 2008). tive Layers Coating (RLC™) process that applies 2 reTypes of Polymer-Coated Controlled-Release Fertilizers Table 1 - Macro nutrient composition (N-P-K) and longevity of polymer-coated controlled release fertilizers commonly used in forest and native plant nurseries * Longevity at 70 oF (21 oC) Osmocote Classic® 3 to 4 mos 14-14-14 19-6-12 Apex® 5 to 6 mos Multicote® Diffusion ® 15-7-15 17-6-17 18-6-18 22-2-3 15-7-15 17-6-17 18-5-18 22-4-9 17-6-17 18-4-18 22-4-8 8 to 10 mos 13-13-13 19-6-12 13-13-13 16-8-16 18-6-12 19-8-12 21-2-11 15-7-15 17-7-14 20-6-12 12 to 14 mos 19-6-12 17-6-12 14-7-14 17-6-14 20-5-12 14 to 16 mos 19-6-12 16-5-11 14-7-14 17-5-14 20-5-10 * = modified from www.scottsprohort.com, www.simplot.com, www.sungro.com, www.diffusionfertilizer.com 6 Forest Nursery Notes Winter 2009 Fertilizer reserves for after sale or outplanting Using long-term PCRF in growing media ensures that plugs will be delivered to the customer with a nutrient reserve (Drahn 2007). For forestry applications, the benefit of this reserve depends on moisture condition on the outplanting site. For example, incorporation of Apex 14 to16 month PCRF in the plugs of Douglas-fir Advantages of Using Polymer-Coated Controlled(Pseudotsuga menziesii) seedlings produced significant Release Fertilizers growth benefits for 2 to 3 years after outplanting on wet sites. However, on a drier site, initial survival of fertilPolymer-coated controlled release fertilizers offer several advantages to nurseries, especially those that grow ized Douglas-fir and ponderosa pine (Pinus ponderosa) seedlings was significantly less than nonfertilized consmall lots of many species or ecotypes: trols and growth after 2 years was the same with or Easy to adjust fertilization type and rate for different without PCRF (Jacobs and others 2003b). crops - With the wide variety of N-P-K formulations and nutrient release timings, growers can easily custom- Cultural Advantages when Using Polymer-Coated ize their fertilization programs. By incorporating differ- Controlled-Release Fertilizers ent PCRF into the soil or batches of growing media, Application method - For the larger volume containers different species or ecotypes can receive the proper used in ornamental nurseries, PCRF are applied in 2 amount of fertilizer at the proper time. ways: incorporation into the growing medium at the time of sowing, and top-dressings during the growing Better fertilizer use efficiency - Placing the fertilizer season. Incorporation into growing media is by far the directly in the root zone is much more efficient than liquid fertilization that is lost when sprayed on benches most common way of using PCRF in the smaller conor walkways, runs off the foliage, or drips through open- tainers used in forest, conservation, and native plant ings in containers. This is particularly true with broad- nurseries. Growers should be mindful of 2 concerns when incorporating PCRF into growing media. The first leaved species that shed a high percentage of applied fertigation. PCRF are ideal for open compounds in rainy concern is to ensure that the small prills are even distributed so that each container has the same number. This climates where applying liquid fertilization to already becomes very problematic with small volume miniplugs, wet plugs is very inefficient. which is why Scotts developed Osmocote® Miniprill Less fertilizer pollution in wastewater - Fertilizers in formulations (Figure 1B). Counting the number of prills nursery runoff, especially N and P, lead to eutrophicaper container or volume of growing media is extremely tion in ditches and ponds. These excess nutrients protedious, but some soil and plant testing laboratories mote the growth of moss and algae on the surface of (www.mmilabs.com or www.qal.us) will perform this soils, growing medium, and floors. Weeds are stimuservice on a fee basis (Pilon and Passchier 2007). The lated by non-target nutrients, and moist, nutrient rich second concern is mechanical damage to the prills that environments are ideal for nursery pests such as fungus can occur when they are mixed with the growing megnats. dium. Overmixing in cement mixers or other mechanical mixers may rupture the polymer-coating and cause No rinsing required after fertilization - After fertiga- an immediate release of fertilizer salts that will not only tion, the concentrated fertilizer solutions need to be damage the mixer but, more importantly, may kill young rinsed off plant foliage to prevent burning (Drahn 2007). germinating seedlings or newly-struck cuttings. Having This extra irrigation can cause more nutrients to leach PCRF incorporated with a ribbon-type mixer is the best from the medium and keeps humidity high in the grow- way to make sure that the prills are evenly distributed ing area, which can create disease problems during and not damaged during the process. Prill damage can cloudy, cool weather. be monitored by taking electrical conductivity measurements of a sample of the growing medium before sowNutrients present at root initiation - When rooting ing. This type of testing is discussed in detail in a subsecuttings, incorporating PCRF into the rooting medium quent section. ensures that nutrients will be available as soon as roots form. This is preferable to fertigation that can keep the During outplanting, PCRF may be placed under or near medium too damp and discourage root formation (Drahn plants (Jacobs and others 2003b). Some researchers 2007). recommend placing PCRF in the bottom of the planting hole, which ensures that released nutrients will be easily Because CRF technology is continually evolving and fertilizer manufacturers are constantly improving the nutrient content and release characteristics of their products, we stress that growers should consult company internet sites for the latest information. 7 Forest Nursery Notes Winter 2009 accessible to the plant (Gleason and others 1990). Other applications include applying the PCRF in a dibbled hole alongside the plant or broadcasting it around its base. To minimize the possibility of fertilizer burn to roots and prevent the nutrients from being “stolen” by competing vegetation, the side application makes the most sense. Variable nutrient release - Laboratory testing in sand columns has shown that the major environmental factor controlling the pattern and longevity of nutrient release from PCRF is the temperature of the soil or growing medium. Most PCRF are based on a standard 70 ºF (21 ºC) benchmark and nutrient release increases or decreases as soil or growing medium temperatures change. Laboratory tests also show that soil moisture has a relatively minor influence on nutrient release within the range typically maintained in container seedling production (Kochba and others 1990). In actual practice, however, nutrients will continue to move outward from the prill as long as an osmotic gradient exists. As the nutrient ions are taken-up by plant roots or leach downward with irrigation, the osmotic gradient becomes higher and more nutrient ions are released (Huett and Gogel 2000). Leaching tests have shown that a certain proportion of total nutrients (10 to 20%) may never release from the PCRF prills because the internal osmotic pressure within the prill decreases as most nutrients are released (Jacobs 2005). Figure 3 - The nutrient release rates were different for 3 brands of polymer-coated controlled- release fertilizers but, in each, phosphorus was released much slower than nitrogen or potassium (A). When the fertilizers were buried in soil, nitrogen ions were released fastest and phosphorus was again the slowest (B). (A - modified from Huett and Gogel 2000, and B - modified from Haase and others 2007). little from their initial levels. They hypothesized that P was inactivated by forming insoluble compounds with the metal micronutrients which remained in the prill When the leaching patterns of 3 brands of PCRF were tested in sand columns (Huett and Gogel 2000), the time membrane. to 90% nutrient release varied among products (Figure 3A). The nutrient release rate was also different for N, The possibility of the slow release of P affecting plant uptake was confirmed when Douglas-fir seedlings were P, and K, which can affect crop development. The slower release of P could be problematic because young fertilized with 3 rates of Osmocote; the foliar N concenplants have a high requirement for P early in the grow- tration increased with fertilization but foliar P decreased ing season. This was confirmed in another leaching trial (Jacobs and others 2003a). As mentioned earlier, this can be compensated for by incorporating another source which concluded that, when PCRF are used, another supplemental source of fertilizer P may be required for of P fertilizer such as concentrated superphoshate (Handreck 1997) or, for container stock, injecting phosearly in the growing season (Handreck 1997) phoric acid into the irrigation system. Of course, the ultimate way to determine if mineral nutrients are being Sand column research is one thing, but nutrient release patterns in soil or growing media could be radically dif- used by plants is to have foliar samples analyzed ferent because of differential adsorption of mineral nu- throughout the growing season (Landis and others trients on cation exchange sites. The Nursery Technol- 2005). ogy Cooperative at Oregon State University buried plastic mesh bags containing PCRF in forest soil and moni- Premature nutrient release causes fertilizer “burn” Research has shown that when PCRF prills are surtored the release of mineral nutrients for more than a rounded by a slightly moist medium they begin nutrient year (Haase and others 2007). Like the sand column studies, they found that the different macronutrients had release, which accelerates under warm conditions. Therefore, PCRF should not be incorporated into growdifferent release rates with N being released the fastest and P the slowest (Figure 3B). The release rate of micro- ing media more than about 2 weeks before it is used. Otherwise, salts can build-up and cause fertilizer burn nutrients was almost nil and the prill content of iron, manganese, zinc, and molybdenum had decreased very when seeds begin to germinate or cuttings begin to root 8 Forest Nursery Notes Winter 2009 Table 2 - Comparison of various techniques of measuring electrical conductivity * EC Technique Saturated Media Extract EC Readings (µS/cm) Containers Soil PCRF 1,000 2,000 3,000 4,000 All but Miniplugs Yes Yes ** 300 700 1,200 1,600 All but Miniplugs Yes No Pour-Through 1,500 2,800 4,200 5,500 All but Miniplugs & Very Large Sizes No Yes Plug Squeeze 1,300 2,700 4,100 5,600 Jiffy, Conetainers, Rootrainers, Miniplugs No No Direct Sensor 700 1,300 1,800 2,400 All but Miniplugs Yes Yes 1:2 Dilution * modified from Fisher and others 2006 ** = vacuum extraction, not squeezing especially with small containers, and more often during hot and dry periods. The ideal situation is to plot EC readings over the course of the growing season to keep track of trends, especially of any accumulation of salts due to insufficient leaching (Figure 4A). (Huett and Gogel 2000). Another potential problem is release of salts when container plants with incorporated PCRF are kept under long-term refrigerated storage. Even though the temperatures are very low, the root plugs are moist and fertilizer salt levels can reach damaging levels, which has been observed during operational cold storage and during a research trial. Ponderosa pine container seedlings were grown with moderate release (12 to 14 mo) or slow release (16 to 20 mo) PCRF and then harvested and stored under refrigeration at 33 °F (0.5 °C) for about 4 months. When a sample of the stored seedlings were subjected to a root growth capacity test, the roots in many of the plugs were completely killed (Fan and others 2004). This type of damage would be hard to detect without the root tests, and affected seedlings could be transplanted or outplanted without any awareness of the problem. Obviously, more research into this potential problem is needed. EC can be measured by several different techniques, but the saturated media extract remains the standard (Landis and Dumroese 2006). Note this restriction on monitoring EC in growing media with incorporated PCRF: any compression or squeezing of the amended medium will force extra nutrients out of the prills and provide erroneous results (Table 2). Catching leachate under the container or using the pour-through technique are good ways to keep track of EC trends for an entire block (Figure 4B) but the readings are just an average of conditions in the various cells. Using a direct sensor is quick and effective in larger containers (Figure 4C) but the probes are too large for use in miniplugs. With senMonitoring nutrient levels with PCRF - The best way sors, it’s critical to always measure EC at the same to avoid problems with PCRF or any fertilizer is through moisture content, such as an hour after irrigation (Scoggins and van Iersel 2006). regular monitoring. All mineral nutrients are taken-up from the solution in the soil or growing medium as fertilizer salts. Therefore, the relative concentration of Using Polymer-Coated Controlled-Release Fertilizers fertilizer salts can be measured with an electrical conin Bareroot Nurseries ductivity (EC) meter. For PCRF, this allows the grower By far, the most work has been done with PCRF in conto monitor precisely when fertilizer is being released from the prills, and Bilderback (2008) recommends that tainer plants but this type of fertilization also has applithe EC should remain in the range of 200 to 500 µS/cm. cation in field soils. In a Wisconsin bareroot nursery, crops of red pine (Pinus resinosa), jack pine (Pinus It’s a good idea to measure EC at least once a month, 9 Forest Nursery Notes Winter 2009 When porous cup lysimeters were installed in pine seedbeds at 3.3 ft (1 m) spacing below the soil surface, nitrate-nitrogen leaching was significantly less with PCRF in the first and second growing seasons compared to standard fertilization (Dobrahner and others 2007). In an Oregon bareroot nursery, nitrate leaching and soil compaction were serious concerns so subsurface banding of polymer-encapsulated sulfur-coated urea was compared to the standard fertilizer top-dressing. The CRF was banded below the soil surface and between the seed rows with a specially-modified seeder (Figure 5A). This allowed roots of seedlings to grow toward the N source and uptake the nutrient without burning (Figure 5B). Subsurface banding eliminated 3 tractor trips per season, which reduced soil compaction in the seedbeds. Because the N was gradually released during the growing season, concerns about nitrate leaching were reduced. As with the Wisconsin nursery, a cost comparison showed that the CRF was less expensive to use because of reductions in application costs, yet seedlings were larger with fewer culls (Steinfeld and Feigner 2004). Figure 4 - Measuring the electrical conductivity of the soil or growing medium is the best way to monitor the effectiveness of polymer-coated controlled-release fertilizers (A). Because extra fertilizer can be squeezed out of the prills, catching leachate (B) or using the pourthrough technique is best for smaller-volume containers. In larger containers and soil, EC can be measured directly with new sensors as long as the measurements are always taken at the same moisture content (C). Summary Of the 3 types of controlled-release fertilizers, polymercoated products are most commonly used in forest, conservation, and native plant nurseries. Depending on the type of coating and temperature of the medium, these fertilizers release their nutrients over periods from 3 to 18 months. For growers, PCRF afford many advantages, including ease of adjusting fertilizer rate for many crops, banksiana), white spruce (Picea glauca), and other conifers are grown on a 2-year schedule. Initial trials with top-dressing Polyon® PCRF had 2 main drawbacks: 1) prills became sticky and didn’t flow well through a typical drop-type fertilizer spreader; and 2) heavy rains washed the prills from the raised seedbeds into the tractor paths. Switching fertilizer brands to Diffusion® (Wilbur-Ellis Company, San Francisco, CA) solved the first problem because the coating did not gum up the fertilizer spreader. A shallow incorporation of the fertilizer into the seedbeds just before sowing and covering the seedbeds with hydromulch solved the problem of the prills washing away. PCRF applications later in the first year and during the second growing season did not wash or blow away because they were held in place by the rows of plants. In a comparison with standard fertilization, PCRF produced satisfactory plants, reduced nitrate leaching, and was more cost effective. Even though PCRF was triple the cost of conventional fertilizer, less frequent applications saved appreciable labor and equipment expenses (Vande Hey 2007). 10 Figure 5 - Polymer-encapsulated urea fertilizer was banded at the time of sowing 3 to 4 inches (7.5 to 10 cm) below the soil and between the seed rows (A). This allowed the seedling roots to access the released nutrients during the growing season without concern about fertilizer burn (B). (From Steinfeld and Feigner 2004). Forest Nursery Notes Winter 2009 better fertilizer use efficiency, and less concern about potential groundwater pollution. In addition, nutrients are more available for germinating seeds or new roots forming on cuttings, and PCRF create fertilizer reserves to be used by the plants after outplanting. In order to achieve uniform and healthy plant growth, it is important to mix PCRF uniformly and without damaging their coatings. The various PCRF products release nutrients differently, but diligent monitoring of electrical conductivity can be used to avoid problems with salt accumulation, or to indicate when supplemental fertigation may be required. Although mainly used in container nurseries, PCRF has been used in bareroot nurseries to produce quality seedlings with less expense. Green Valley Agricultural. 2008. Diffusion controlled release fertilizers. URL: http:// www.diffusionfertilizer.com/7128.html (accessed 11 Dec 2008). References Hulme F, Buchheit C. 2007. The Value in Osmocote® Controlled Release Technology. The Scotts Exchange Tech Shares. URL: http://www.scottsprohort.com (accessed 25 Nov 2008). 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Soil Science 172(3): 242 Fort Collins (CO): USDA Forest Service, Rocky Mountain Research Station. Proceedings RMRS-P-35. p 113-255. 118. Drahn SR. 2007. Propagating with Controlled Release Fertilizer. Presentation at 2007 Western IPPS Regional Jacobs DF, Rose R, Haase DL. 2003a. Development of Douglas-fir seedling root architecture in response to Meeting. Salem, OR. URL: http://www.ippswr.org/ home/ippsna/2007/Presentations/Drahn.pdf (accessed 8 localized nutrient supply. Canadian Journal of Forest Research 33: 118–125. Dec 2008). Fan Z, Moore JA, Wenny DL. 2004. Growth and nutrition of container-grown ponderosa pine seedlings with controlled-release fertilizer incorporated in the root plug. Annals of Forest Science 61(2):117-124. Fisher PR, Douglas AC, Argo WR. 2006. How to soil test small containers. GM Pro 26(03): 46-47, 49-50, 52. Gambash S, Kochba M, Avnimelech Y. 1990. Studies on slow release fertilizers. II. 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Plant nutrient testing and analysis in forest and conservation nurseries. IN: Dumroese RK, Riley LE, Landis TD, technical coordinators. National proceedings, forest and conservation nursery associations–2004. Fort Collins (CO): USDA Forest Service, Rocky Mountain Research Station. Proceedings RMRS-P-35. p 76-84. 11 Forest Nursery Notes Winter 2009 Pilon P, Passchier G. 2007. Talking temperature. Greenhouse Grower 25(10):49-50. Scotts Horticulture. 2008. Controlled release fertilizers. URL: http://the-scotts-exchange.com/products/ fertilizers/osmocote.cfm (accessed 3 Dec 2008). Scoggins HL, van Iersel MW. 2006 In situ probes for measurement of electrical conductivity of soilless substrates: effects of temperature and substrate moisture content. HortScience 41: 210-214. Simplot. 2008. Apex nursery fertilizer: a higher standard in plant nutrition. URL: http://www.simplot.com/turf/ apex/index.cfm (accessed 3 Dec 2008). Steinfeld D, Feigner S. 2004. Subsurface banding of phosphorus, potassium, and controlled release nitrogen fertilizers in the 1+0 year at J. Herbert Stone Nursery. In: National proceedings: forest and conservation nursery associations–2003. Fort Collins (CO): USDA Forest Service, Rocky Mountain Research Station. Proceedings RMRS-P-33. p 33-37. Sungrow Horticulture. 2008. Nutricote controlled release fertilizer. URL: http://www.sungro.com/ products_displayProBrand.php?brand_id=6 (accessed 3 Dec 2008). Vande Hey JM. 2007. Production of conifer bareroot seedlings using controlled release fertilizer. Native Plants Journal 8(3):288-293. 12